Restructured transactivation domain in hamster AH receptor

Hamsters and Han/Wistar (Kuopio; H/W) rats show peculiarly selective responsiveness to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). They are extremely resistant to its acute lethality but sensitive to, e.g. , enzyme induction. The biological effects of TCDD are mediated by the AH receptor (AHR). Recent studies on H/W rat AHR discovered a remodelled transactivation domain which appears to be critical for the TCDD resistance of these animals. Here, molecular cloning and sequencing of hamster AHR reveals another type of restructured transactivation domain. In hamsters, the functionally pivotal Q-rich region is substantially expanded and enriched in glutamine compared with all other AHRs cloned to date. By contrast, the amino-terminal end is highly conserved, which is in agreement with the H/W rat AHR. Because of the additional material in the transactivation domain, hamster AHR protein is larger than that in rats or mice, but the pattern of AHR mRNA expression in tissues is similar.     

Polymorphisms in the human AH receptor

The AH receptor (AHR) mediates toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) as well as induction of three cytochrome P450 enzymes and certain Phase II enzymes. In laboratory animals, genetic variations in the AHR lead to substantial differences in sensitivity to biochemical and toxic effects of TCDD and related compounds. Relatively few polymorphisms have been discovered in the human AHR gene; these occur predominantly in exon 10, a region that encodes a major portion of the transactivation domain of the receptor that is responsible for regulating expression of other genes. In human populations there is a wide range of variation in responses regulated by the AHR for example, induction of CYP1A1. Some variation in human responsiveness likely is due to genetically based variations in AHR structure. Thus far, however, only one pair of polymorphisms, those at codons 517 and 570, has been shown to have a clear cut and strong effect on the phenotype of an AHR-mediated response. The search continues for polymorphisms that alter AHR function because this receptor is a central factor in determining responses to important environmental contaminants and also plays a physiologic role in early development in mammals.     

Primary structure and inducibility by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) of aryl hydrocarbon receptor repressor in a TCDD-sensitive and a TCDD-resistant rat strain

The aryl hydrocarbon receptor repressor (AHRR) is a negative regulator of AH receptor (AHR), which mediates most of the toxic and biochemical effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). AHR has been shown to be the major reason for the exceptionally wide (ca. 1000-fold) sensitivity difference in acute toxicity of TCDD between two rat strains, sensitive Long-Evans (Turku/AB) (L-E) and resistant Han/Wistar (Kuopio) (H/W), but there is another, currently unknown contributing factor involved. In the present study, we examined AHRR structure and expression in these rat strains to find out whether AHRR could be this auxiliary factor. Molecular cloning of AHRR coding region showed that consistent with AHRR proteins in other species, the N-terminal end of rat AHRR is highly conserved, but PAS B and Q-rich domains are severely truncated or lacking. Identical structures were recorded in both strains. Next, the time-, dose-, and tissue-dependent expression of AHRR was determined using quantitative real-time RT-PCR. In liver, AHRR expression was very low in untreated rats, but it increased rapidly after TCDD exposure (100microg/kg). Testis exhibited the highest constitutive expression of AHRR, whereas kidney, spleen, and heart showed the highest induction of AHRR in response to TCDD treatment. Again, no marked differences were found between H/W and L-E rats, implying that AHRR is not the auxiliary contributing factor to the strain difference in TCDD sensitivity. However, simultaneous measurement of CYP1A1 mRNA reinforced the view that AHRR is an important determinant of tissue-specific responsiveness to TCDD.     

Expression of the mediators of dioxin toxicity,aryl hydrocarbon receptor (AHR) and the AHR nuclear translocator (ARNT), is developmentally regulated in mouse teeth

Dioxins are persistent and ubiquitous environmental poisons that become enriched in the food chain. Besides being acutely lethal, the most toxic dioxin congener, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), is developmentally toxic to many animal species. We have previously found that developing teeth of children may be sensitive to environmental dioxins via their mother's milk and that rat and mouse teeth are dioxin-sensitive throughout their development. The aryl hydrocarbon receptor (AHR) together with the AHR nuclear translocator (ARNT) protein is believed to mediate the toxic effects of dioxins. To study the potential involvement of the AHR-ARNT pathway in the dental toxicity of TCDD, we analysed the expression of AHR and ARNT by in situ hybridization and immunohistochemistry in developing mouse teeth. AHR mRNA first appeared in the epithelium of E12 first molar tooth buds and both proteins were weakly expressed in the bud. After cytodifferentiation the expression was up regulated and became intense in secretory odontoblasts and ameloblasts. The coexpression of AHR and ARNT during early tooth development as well as during the information and mineralization of the dental matrices is suggestive of the AHR-ARNT pathway as a mediator of dental toxicity of TCDD.     

An aryl hydrocarbon receptor (AHR) homologue from the soft-shell clam, Mya arenaria: evidence that invertebrate AHR homologues lack 2,3,7,8-tetrachlorodibenzo-p-dioxin and beta-naphthoflavone binding.

The aryl hydrocarbon receptor (AHR) mediates numerous toxic effects following exposure of vertebrate animals to certain aromatic environmental contaminants, including 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). To investigate possible effects of TCDD on invertebrates, a cDNA encoding an AHR homologue was cloned from the soft-shell clam, Mya arenaria. The predicted amino acid sequence contains regions characteristic of vertebrate AHRs: basic helix-loop-helix (bHLH) and PER-ARNT-SIM (PAS) domains and a glutamine-rich region. Phylogenetic analysis shows that the clam AHR sequence groups within the AHR subfamily of the bHLH-PAS family, in a clade containing AHR homologues from Drosophila melanogaster and Caenorhabditis elegans. AHR mRNA expression was detected in all tissue types tested: adductor muscle, digestive gland, foot, gill, gonad, mantle, and siphon. The in vitro-expressed clam AHR exhibited sequence-specific interactions with a mammalian xenobiotic response element (XRE). Velocity sedimentation analysis using either in vitro-expressed clam AHR or clam cytosolic proteins showed that this AHR homologue binds neither [(3)H]TCDD nor [(3)H]beta-naphthoflavone (BNF). Similarly, in vitro-expressed D. melanogaster and C. elegans AHR homologues lacked specific binding of these compounds. Thus, the absence of specific, high-affinity binding of the prototypical AHR ligands TCDD and BNF, is a property shared by known invertebrate AHR homologues, distinguishing them from vertebrate AHRs. Comparative studies of phylogenetically diverse organisms may help identify an endogenous ligand(s) and the physiological role(s) for this protein.     

Autoradiographic localization of aromatic hydrocarbon receptor (AHR) in rhesus monkey ovary

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is the most toxic congener of a large class of manmade pollutants that persist in the environment. TCDD exerts its toxic effects, in part, by binding to its receptor known as the aromatic hydrocarbon receptor (AHR). TCDD is estrogen modulatory and in some systems its receptor associates directly with estrogen receptors via co-activator molecules. TCDD inhibits steroid synthesis in human ovarian granulosa cells and AHR is found in these cells. We have previously shown that AHR is found in whole rhesus monkey ovary, but have yet to establish its location. In the present study, we set out to show that radiolabeled TCDD binds to monkey ovarian follicles and that this binding is receptor mediated. Ovaries from Macaca mulatta were sectioned on a cryostat at 10 micro m; and sections were incubated with either control vehicle, (3)H-TCDD, or (3)H-TCDD plus alpha-naphthoflavone (ANF), a known receptor-blocking agent. Here, we show for the first time specific binding of TCDD to the granulosa cells of antral follicles and other regions of the rhesus monkey ovary. Our data indicate a 60-fold increase in binding with (3)H-TCDD over that of control, and that this binding is reduced to the levels seen in controls with the addition of the competitive antagonist ANF. These findings support the hypothesis that TCDD directly affects primate ovarian function via the AHR.     

Molecular evidence predicts aryl hydrocarbon receptor ligand insensitivity in the peregrine falcon (<Emphasis Type="Italic">Falco peregrines</Emphasis>)

Some wild populations of fish-eating birds and raptors are exposed to high concentrations of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related compounds such as other 2,3,7,8-substituted polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans and coplanar polychlorinated biphenyls, resulting in accumulation in their tissues. It has been demonstrated that TCDD-like chemicals cause toxic effects via aryl hydrocarbon receptor (AHR)-mediated signaling pathways. The aim of this study was to characterize the AHR from the peregrine falcon (Falco peregrines) to predict its sensitivity to TCDD-like chemicals. The AHR1, AHR2, and AHR nuclear translocator 1 of the peregrine falcon are more similar in amino acid sequence to avian species less sensitive to TCDD-like chemicals such as the cormorant (95%) than to more sensitive species such as the chicken (90%). From the amino acid sequence, it is likely that the ligand-binding affinity of peregrine falcon AHR1 and AHR2 would be very low compared with the chicken or other sensitive species, and it was actually proved by an in vitro reporter gene assay. We concluded that the peregrine falcon, one of raptor species, may be relatively resistant to TCDD-like chemicals.     

Identification of novel splice variants of ARNT and ARNT2 in the rat

Most of the biochemical and toxic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) are mediated by the bHLH/PAS protein AH receptor (AHR). For regulation of gene activities, AHR dimerizes with another member of the bHLH/PAS protein family, AHR nuclear translocator (ARNT). A substrain of Wistar rats, Han/Wistar (Kuopio) (H/W), is about 1000-fold more resistant to the acute lethality of TCDD than other strains, exemplified by Long-Evans (Turku/AB) (L-E); the LD50 values for these two strains are >9600 and 10-20 microg/kg, respectively. Previous studies have demonstrated that the major reason for the exceptional TCDD resistance of H/W rats lies in their AHR, which is remodeled at its C-terminal transactivation domain, but there appears to be another contributing gene product. The present study set out to compare the primary structure of ARNT and the closely related ARNT2 proteins in H/W and L-E rats by cDNA cloning. To our surprise, we found several isoforms of these proteins only one of which has previously been reported in rats. All of the isoforms appeared to arise from alternative splicing. For ARNT, isoforms with deletions at exon 5, 3(') end of exon 6 or 5(') end of exon 11, or with an insertion at 5(') end of exon 20 were discovered. There was also interindividual variation in the number of glutamine-encoding codons at 5(') end of exon 16. The most exciting new variant was revealed for ARNT2, because the insertion found at 5(') end of exon 19 disrupts the functionally critical transactivation domain in the protein, implying a dominant negative role for this isoform. The relative expression levels of the variants did not differ in the two rat strains, nor did TCDD modify the ratios, suggesting that the variants do not contribute to TCDD resistance. However, the regulation of ARNT and ARNT2 activities may be more intricate than previously assumed.     

The hepatic Ah receptor for 2,3,7,8-tetrachlorodibenzo-p-dioxin: species differences in subunit dissociation

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD, dioxin) produces many of its biological effects by binding to a soluble, intracellular protein (the Ah receptor (AhR]. The hepatic AhR, from a variety of species, is present in low salt cytosol as a form which sediments at 8-10 S. High salt (0.4 M KCL) dissociates the rat, guinea pig, and rabbit cytosolic TCDD:AhR complex to a form which sediments at 5-6 S. In contrast, high salt conditions failed to dissociate the 8-10 S TCDD:AhR complex present in any of the mouse strains studied. Incubation of cytosol with heparin resulted in a shift of the [3H]TCDD:AhR complex to a smaller sedimenting form in all species. Mouse TCDD:AhR complex sedimented at 8-10 S when cytosol was simultaneously incubated with high salt and heparin, indicating that the interaction of heparin with the AhR was electrostatic in nature. Incubation of heparin-dissociated mouse TCDD:AhR complex (5-6 S) with high salt resulted in reassociation of AhR to a form which sediments at 8-10 S. Our data suggests that the resistance of mouse AhR to salt-mediated dissociation may be due to a property of the receptor protein itself and also indicates that mouse hepatic cytosolic AhR is distinctly different from that present in all other species examined to date.